A new chapter in the bisphenol A story: bisphenol S and bisphenol F are not safe alternatives to this compound

Bisphenol A (BPA) is a widely studied typical endocrine-disrupting chemical, and one of the major new issues is the safe replacement of this commonly used compound. Bisphenol S (BPS) and bisphenol F (BPF) are already or are planned to be used as BPA alternatives. With the use of a culture system that we developed (fetal testis assay [FeTA]), we previously showed that 10 nmol/L BPA reduces basal testosterone secretion of human fetal testis explants and that the susceptibility to BPA is at least 100-fold lower in rat and mouse fetal testes. Here, we show that addition of LH in the FeTA system considerably enhances BPA minimum effective concentration in mouse and human but not in rat fetal testes. Then, using the FeTA system without LH (the experimental conditions in which mouse and human fetal testes are most sensitive to BPA), we found that, as for BPA, 10 nmol/L BPS or BPF is sufficient to decrease basal testosterone secretion by human fetal testes with often nonmonotonic dose-response curves. In fetal mouse testes, the dose-response curves were mostly monotonic and the minimum effective concentrations were 1,000 nmol/L for BPA and BPF and 100 nmol/L for BPS. Finally, 10,000 nmol/L BPA, BPS, or BPF reduced Insl3 expression in cultured mouse fetal testes. This is the first report describing BPS and BPF adverse effects on a physiologic function in humans and rodents

Effects of environmental Bisphenol A exposures on germ cell development and Leydig cell function in the human fetal testis

<div><p>Background</p><p>Using an organotypic culture system termed human Fetal Testis Assay (hFeTA) we previously showed that 0.01 μM BPA decreases basal, but not LH-stimulated, testosterone secreted by the first trimester human fetal testis. The present study was conducted to determine the potential for a long-term antiandrogenic effect of BPA using a xenograft model, and also to study the effect of BPA on germ cell development using both the hFETA and xenograft models.</p><p>Methods</p><p>Using the hFeTA system, first trimester testes were cultured for 3 days with 0.01 to 10 μM BPA. For xenografts, adult castrate male nude mice were injected with hCG and grafted with first trimester testes. Host mice received 10 μM BPA (~ 500 μg/kg/day) in their drinking water for 5 weeks. Plasma levels of total and unconjugated BPA were 0.10 μM and 0.038 μM respectively. Mice grafted with second trimester testes received 0.5 and 50 μg/kg/day BPA by oral gavage for 5 weeks.</p><p>Results</p><p>With first trimester human testes, using the hFeTA model, 10 μM BPA increased germ cell apoptosis. In xenografts, germ cell density was also reduced by BPA exposure. Importantly, BPA exposure significantly decreased the percentage of germ cells expressing the pluripotency marker AP-2γ, whilst the percentage of those expressing the pre-spermatogonial marker MAGE-A4 significantly increased. BPA exposure did not affect hCG-stimulated androgen production in first and second trimester xenografts as evaluated by both plasma testosterone level and seminal vesicle weight in host mice.</p><p>Conclusions</p><p>Exposure to BPA at environmentally relevant concentrations impairs germ cell development in first trimester human fetal testis, whilst gonadotrophin-stimulated testosterone production was unaffected in both first and second trimester testis. Studies using first trimester human fetal testis demonstrate the complementarity of the FeTA and xenograft models for determining the respective short-term and long term effects of environmental exposures.</p></div

CD117hi expression identifies a human fetal Hematopoietic Stem Cell population with high proliferation and self-renewal potential

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Effect of BPA exposure on plasma BPA concentration in xenografted mice.

<p>Plasma levels of BPA were quantified by gas chromatography coupled to tandem mass spectrometry (GC-MS/MS) from castrated Nude male mice xenografted with first trimester human fetal testis (9.1–11.3 GW, mean 10.2 ± 0.2 GW; n = 6–7) and exposed to vehicle (Control) or BPA (10 μM in the drinking water) for five weeks. For each fetus, all the pieces from one testis were grafted in a control mouse and all the pieces from the contralateral testis were grafted in a BPA-treated mouse. Statistical analysis was performed using the Mann-Whitney test. *p<0.05, **p<0.01.</p

Effect of BPA exposure on germ cell apoptosis and proliferation in first trimester human fetal testes cultured using the FeTA system.

<p>Human fetal testes (6–12 GW, mean 8.7 ± 0.6 GW) were cultured using the ex vivo <u>h</u>uman <u>Fe</u>tal <u>T</u>estis <u>A</u>ssay system (hFeTA). After 24 hours in control medium, explants were cultured with 100 ng/mL of LH for the 3 subsequent days in the presence of ethanol vehicle (control explants) or BPA at concentrations ranging from 0.01 to 10 μM. Control and BPA-treated explants were paired samples from the same testis. (A) Histological sections after labeling with anti-cleaved caspase-3 antibody (brown) and anti-AMH antibody (green). Positive (red arrows) and negative (black arrows) germ cells can be identified. Scale bar: 10 μm. (B) Quantification of cleaved caspase-3 positive cells (mean ± SEM; n = 4–8). (C) Histological sections after labeling with anti-Ki-67 antibody (brown) and anti-AMH antibody (green). Positive (red arrows) and negative (black arrows) germ cells can be identified. Scale bar: 50 μm. (D) Quantification of Ki67 positive gonocytes (mean ± SEM; n = 4–8).</p

Effect of BPA exposure on germ cell differentiation in first trimester human fetal testis xenografts.

<p>Human fetal testes (9.1–11.3 GW) were xenografted into castrate Nude (host) mice. Host mice received vehicle (Control) or 10μM BPA in the drinking water for five weeks. (A) Histological sections of testes after immunostaining for AP-2γ (gonocytes). Positive (red arrows) and negative (black arrows) germ cells can be identified. Scale bar: 60 μm. (B) Quantification of AP-2γ-positive cells displayed as mean ± SEM (n = 9) on the left panel and as individual values with a line drawn between the control and the corresponding BPA-treated testis from the same fetus on the right panel. (C) Histological sections of testes after immunostaining for MAGE-A4 (prespermatogonia). Positive (red arrows) and negative (black arrows) germ cells can be identified. Scale bar: 60 μm. (D) Quantification of MAGE-A4-positive cells displayed as mean ± SEM (n = 8) on the left part and as individual values with a line drawn between the control and the corresponding BPA-treated testis from the same fetus on the right part. Data analyzed using the Wilcoxon paired-test. *p<0.05, **p<0.01.</p

Xenografting first trimester human fetal testis.

<p>Human fetal testes (9.1–11.3 GW) xenografted in castrated Nude (host) mice. Host mice received vehicle (Control) or 10μM BPA in the drinking water. (A) Host mouse six weeks after xenografting demonstrating xenograft tissue below the skin (green circles). (B) Xenografted explants (green circles) in the back muscle of the host mouse at the end of the experiment, in a control and a BPA-treated mouse. Scale bar: 5 mm. (C) Histological section of a xenograft after haematoxylin-eosin-saffron staining, T: testis; M: mouse muscle; C: connective tissue. Scale bar: 100 μm. (D) Histological section of a xenograft showing a blood vessel (BV) in the interstitial tissue. LC: Leydig cell. Scale bar: 10 μm.</p

Effect of BPA exposure on germ cell density in first trimester human fetal testis xenografts.

<p>Human fetal testes (9.1–11.3 GW) were xenografted into castrate Nude (host) mice. Host mice received vehicle (Control) or 10μM BPA in the drinking water for five weeks. (A) Histological sections after haematoxylin-eosin-saffron staining. Germ cells (black arrow) can be easily identified. Scale bar: 20 μm. (B) Quantification of germ cell density displayed as mean ± SEM (n = 9) on the left panel and as individual values with a line drawn between the control and the corresponding BPA-treated testis from the same fetus on the right panel. Data analyzed using the Wilcoxon paired-test. *p<0.05 compared with control condition.</p

Effect of BPA exposure on plasma testosterone level and seminal vesicle weight in the host mice xenografted with first trimester human testes and on steroidogenic genes expression in the xenografts.

<p>Human fetal testes (9.1–11.3 GW) were xenografted into castrate Nude (host) mice. Host mice received vehicle (Control) or 10 μM BPA in the drinking water for five weeks. (A) seminal vesicle weight displayed as mean ± SEM (n = 6) on the left panel and as individual values with a line drawn between the control and the corresponding BPA-exposed testis from the same fetus on the right panel. B) plasma testosterone concentration in host mice displayed as mean ± SEM (n = 6) on the left panel and as individual values with a line drawn between the control and the corresponding BPA-exposed testis from the same fetus on the right panel. C) Expression of key genes in the steroidogenic pathway (STAR, CYP11A1, CYP17A1 and CYP19) using quantitative RT-PCR standardized to either β-ACTIN (ACTIN) or RPLP0 or CYPA as endogenous control. Results are presented as a percentage of the control value (mean ± SEM; n = 4). Data analyzed by Wilcoxon test. No significant difference between BPA-treated and control mice were identified.</p

Effect of BPA exposure on testosterone plasma level and seminal vesicle weight in the host mice carrying second trimester human fetal testis xenografts.

<p>Human fetal testes (14-18GW) xenografted into castrated Nude (host) mice. Each human fetal testis was grafted into 1–3 host mice which received the same treatment. Host mice received vehicle (Control), BPA (0.5μg/kg or 50μg/kg/d) daily by oral gavage for five weeks. A) seminal vesicle weight as overall mean ± SEM (n = 4) is displayed on the left with individual values on the right. B) plasma testosterone concentration in host mice as overall mean ± SEM (n = 4) is displayed on the left with individual values on the right. Data analysed by Mann-Whitney test. No significant differences were observed for serum testosterone or seminal vesicle weight between BPA-treated mice compared to control.</p